How a Landfill Works Presented By: American Environmental Landfill, Inc

Total Page:16

File Type:pdf, Size:1020Kb

How a Landfill Works Presented By: American Environmental Landfill, Inc How a Landfill Works Presented by: American Environmental Landfill, Inc. 1420 W. 35th Street, Suite B Tulsa, OK 74107 Phone: 918-245-7786 Fax: 918-245-7774 How a Landfill Works So you have just finished your meal at a fast food restaurant and you throw your uneaten food, food wrappers, drink cup, utensils and napkins into the trash can. Odds are you don’t think about that waste again. On trash pickup day in your neighborhood, you push your can out to the curb, and workers dump the contents into a big truck and haul it away. You don’t have to think about that waste again, either. But maybe you have wondered, as you watch the trash truck pull away, just where that garbage ends up. Americans generate trash at an astonishing rate of four to seven pounds per day per person, which translates to at least 600,000 tons per day or at least 210 million tons per year! This is almost twice as much trash per person as most other major countries. What happens to this trash? Some gets recycled or recovered and some is burned, but the majority is buried in landfills. In this overview of how a landfill works, we will examine how a landfill is made, what happens to the trash in landfills, what risks are associated with a landfill and how these risks are solved. How is Trash Disposed of? The trash production in the United States has almost tripled since 1960 (Figure 2). This trash is handled in various ways. About 27 % of the trash is recycled or composted, 16% is burned and 57% is buried in landfills. The amount of trash buried in landfills has doubled since 1960. The United States ranks about in the middle of the major countries (United Kingdom, Canada, Germany, France and Japan) in landfill disposal. The United Kingdom ranks highest, burying about 90 percent of its solid waste in landfills. 2 What is a Landfill? There are two ways to bury trash: • Dump - an open hole in the ground where trash is buried, often full of various pests and animals including rats, mice and birds. (This is most people’s idea of a landfill!) • Landfill - carefully designed structure built into or on top of the ground in which trash is isolated from the surrounding environment (groundwater, air, rain). This isolation is accomplished with a bottom liner and daily covering of soil. • Sanitary landfill - landfill that uses a clay liner to isolate the trash from the environment. • Municipal solid waste (MSW) landfill - uses a synthetic (plastic) liner to isolate the trash from the environment. The purpose of a landfill is to bury he trash in such a way that it will be isolated from groundwater, will be kept dry and will not be in contact with air. Unlike a compost pile, a landfill is designed to keep the trash away from people, but does not allow it to decompose quickly. Proposing the Landfill For a landfill to be built, the operators have to make sure that they follow certain steps. In most parts of the world, there are regulations that govern where a landfill can be placed and how it can operate. The whole process begins with someone proposing the landfill. In the United States, taking care of trash and building landfills are local government responsibilities. Before a city or other authority can build a landfill, an environmental impact study must be done on the proposed site to determine: • The area of land necessary for the landfill • The composition of the underlying soil and bedrock • The flow of surface water over the site • The impact of the proposed landfill on the local environment and wildlife • The historical or archaeological value of the proposed site Once the environmental impact study has been completed, permits must be obtained from the local, state and federal governments. In addition, money will have to be raised from taxes or municipal bonds to build and operate the landfill if it is owned by the government. In that case, funding will come from some public source; therefore public approval must be obtained through local governments or a referendum. Otherwise, landfills have to be constructed and managed by free enterprise and small business owners. 3 Building the Landfill Once the environmental impact study is complete, the permits are granted and the money has been raised (be it public or private funds), construction begins. First, access roads to the landfill site must be built if they do not already exist. These roads will be used by construction equipment, sanitation services and the general public. After roads have been built, then the landfill can be excavated. Parts of a Landfill This cross-section drawing shows the structure of a municipal solid waste landfill. The arrows indicate the flow of leachate, which is contaminated substances. The basic parts of a landfill, as shown in Figure 1, are: • Bottom liner system - separates trash and subsequent leachate from groundwater • Cells (old and new) - where the trash is stored within the landfill • Storm water drainage system - collects rain water that falls on the landfill • Leachate collection system - collects water that has percolated through the landfill itself and contains contaminating substances (leachate) • Methane collection system - collects methane gas that is formed during the breakdown of trash • Covering or cap - seals off the top of the landfill Figure 1 Structure of a Municipal Solid Waste Landfill; the arrows indicate the flow of leachate Each of these parts is designed to address specific risks that are encountered in a landfill. So, as we discuss each part of the landfill, we’ll explain what risk is solved. A Ground Water B Compacted Clay C Plastic Liner D Leachate Collection Pipe E Geotextile Mat F Gravel G Drainage Layer H Soil Layer I Old Cells J New Cells K Leachate Pond Figure 1 Structure of a Municipal Solid Waste Landfill; the arrows indicate the flow of leachate 4 Bottom Liner System A landfill’s major purpose and one of its biggest challenges is to contain the trash so that the trash doesn’t cause problems in the environment. The bottom liner prevents the trash from coming in contact with the outside soil, particularly the groundwater. In MSW landfills, the liner is usually some type of durable, puncture-resistant synthetic plastic (polyethylene, high-density polyethylene, polyvinylchloride). It is usually 30-100 mils thick. The plastic liner may be also be combined with compacted clay soils as an additional liner and surrounded on either side by a fabric mat (geotextile mat) that will help to keep the plastic liner from tearing or puncturing from the nearby rock and gravel layers. Cells (Old and New) Perhaps, the most precious commodity and overriding risk in a landfill is air space. The amount of space is directly related to the capacity and usable life of the landfill. If you can increase the air space, then you can extend the usable life of the landfill. To do this, trash is compacted into areas, called cells, that contain only one day’s amount of trash. Trash within cells are compressed by using heavy equipment (tractors, bulldozers, rollers and graders) that go over the mound of trash several times). Once the cell is made, it is covered with six inches of soil and compacted further. Cells are arranged in rows and layers of adjoining cells (lifts). In addition to compressing the trash into cells, space is conserved by excluding bulky materials, such as carpets, mattresses, foam and yard waste, from the landfill. Storm Water Drainage It is important to keep the landfill as dry as possible to reduce the amount of leachate. This can be done in two ways: • Exclude liquids from the solid waste. Solid waste must be tested for liquids before entering the landfill. This is done by passing samples of the waste through standard paint filters. If no liquid comes through the sample after 10 minutes, then the trash is accepted into the landfill. • Keep rainwater out of the landfill. To exclude rainwater, the landfill has a storm drainage system. Plastic drainage pipes and storm liners collect water from areas of the landfill and channel it to drainage ditches surrounding the landfill’s base. The ditches are either concrete or gravel-lined and carry water to collection ponds to the side of the landfill. In the collection ponds, suspended soil particles are allowed to settle, and the water is tested for leachate chemicals. Once settling has occurred and the water has passed tests, it is then pumped or allowed to flow off-site. 5 Leachate Collection System No system to exclude water from the landfill is perfect and water does get into the landfill. The water percolates through the cells and soil in the landfill much as water percolates through ground coffee in a drip coffee maker. As the water percolates through the trash, it picks up contaminants (organic and inorganic chemicals, metals, biological waste products of decomposition) just as water picks up coffee in the coffee maker. This water with the dissolved contaminants is called leachate and is typically acidic. To collect leachate, perforated pipes run throughout the landfill. These pipes then drain into a leachate pipe, which carries leachate to a collection pond. Leachate can be pumped to the collection pond or flow to it by gravity. The leachate in the pond is tested for acceptable levels of various chemicals (biological and chemical oxygen demands, organic chemicals, pH, calcium, magnesium, iron, sulfate and chloride) and allowed to settle. After testing, the leachate must be treated like any other sewage/ wastewater; the treatment may occur on-site or off-site.
Recommended publications
  • State of Utah DIVISION of WASTE MANAGEMENT GARY R
    Department of Environmental Quality L. Scott Baird Executive Director State of Utah DIVISION OF WASTE MANAGEMENT GARY R. HERBERT AND RADIATION CONTROL Governor Ty L. Howard SPENCER J. COX Director Lieutenant Governor November 5, 2020 Cassady Kristensen Environmental Business Partner Rio Tinto Kennecott 4700 Daybreak Parkway South Jordan, UT 84009 RE: Kennecott Utah Copper Tailings Impoundment Refuse Class IIIb Landfill Permit Dear Ms. Kristensen: The Division of Waste Management and Radiation Control (Division) has completed its review of the application to permit the Rio Tinto Kennecott Utah Copper Tailings Impoundment Refuse Class IIIb Landfill located on the Rio Tinto Kennecott Tailings Impoundment facility in Salt Lake County, Utah. Enclosed with this letter is the approved Permit Number 1905 and applicable attachments from portions of the application. The Permit approval and expiration dates are shown on the permit cover page. Also, the Statement of Basis for this permit (DSHW-2020-014707) is included with the permit. If you have any questions, please call Doug Taylor at (801) 536-0240. Sincerely, Ty L. Howard, Director Division of Waste Management and Radiation Control (Over) DSHW-2020-014711 195 North 1950 West • Salt Lake City, UT Mailing Address: P.O. Box 144880 • Salt Lake City, UT 84114-4880 Telephone (801) 536-0200 • Fax (801) 536-0222 • T.D.D. (801) 536-4284 www.deq.utah.gov Printed on 100% recycled paper TLH/DT/ar Enclosures: Permit (DSHW-2020-004084) Attachment #1 - Landfill Design (DSHW-2020-004510) Attachment #2 – Operation Plan (DSHW- 2020-004512) Attachment #3 – Closure and Post-Closure Plan (DSHW-2020-004514) Statement of Basis (DSHW-2020-014707) c: Gary Edwards, MS, Health Officer, Salt Lake County Health Dept.
    [Show full text]
  • Contaminated Soil in Gardens
    Contaminated Soil in Gardens How to avoid the harmful effects EUR/ICP/LVNG 03 01 02(A) E64737 EUROPEAN HEALTH21 TARGET 11 HEALTHIER LIVING By the year 2015, people across society should have adopted healthier patterns of living (Adopted by the WHO Regional Committee for Europe at its forty-eighth session, Copenhagen, September 1998) Abstract In many cities, gardens are located on old, abandoned landfills and dumping sites. Cities have expanded by filling up spaces around the city with garbage, rubble and earth. The places where old landfills were have often become gardens where citizens can get away and enjoy the open air away from the noise and racket of cities. Normal garbage and rubble in landfills do not present a problem, however industrial and chemical waste can present a health hazard, especially when concentrations of contaminants are above acceptable limits. Some special precautions are proposed in this booklet so that the potential ill effects of contaminated soil can be avoided. Keywords SOIL POLLUTANTS RISK MANAGEMENT GUIDELINES URBAN HEALTH Contents The soil is contaminated – what then? .......................................................1 What is in the ground under us?.................................................................2 How harmful substances may affect the body ............................................3 How to reduce the risk................................................................................4 The best way to garden..............................................................................5
    [Show full text]
  • Municipal Solid Waste Landfill Operation and Management Workbook
    MUNICIPAL SOLID WASTE LANDFILL OPERATION AND MANAGEMENT WORKBOOK Revised April 2018 Preface In many ways, constructing, operating and maintaining a municipal solid waste landfill is similar to constructing, operating, and maintaining a highway, dam, canal, bridge, or other engineered structure. The most important similarity is that landfills, like other engineered structures, must be constructed and operated in a manner that will provide safe, long-term, and reliable service to the communities they serve. Proper design, construction, operation, monitoring, closure and post-closure care are critical because after disposal the waste can be a threat to human health and the environment for decades to centuries. This workbook is intended to provide municipal landfill operators and managers in Wyoming with the fundamental knowledge and technical background necessary to ensure that landfills are operated efficiently, effectively, and in a manner that is protective of human health and the environment. This workbook contains information regarding basic construction and operation activities that are encountered on a routine basis at most landfills. The basic procedures and fundamental elements of landfill permitting, construction management, monitoring, closure, post-closure care, and financial assurance are also addressed. The workbook includes informative tips and information that landfill operators and managers can use to conserve landfill space, minimize the potential for pollution, reduce operating costs, and comply with applicable rules and regulations. In addition to this workbook, operators and managers need to become familiar with the Wyoming Solid Waste Rules and Regulations applicable to municipal solid waste. The DEQ also provides numerous guidelines that may help understand regulatory requirements in more detail.
    [Show full text]
  • Five Facts About Incineration Five Facts About Incineration
    Five facts about incineration Five facts about incineration Across the globe, cities are looking for ways to improve their municipal solid waste systems. In the search for services that are affordable, green and easy to implement, many cities are encouraged to turn to waste-to-energy (WtE) technologies, such as incineration.1 But, as found in WIEGO’s Technical Brief 11 (Waste Incineration and Informal Livelihoods: A Technical Guide on Waste-to-Energy Initiatives by Jeroen IJgosse), incineration is far from the perfect solution and, particularly in the Global South, can be less cost-effective, more complicated and can negatively impact the environment and informal waste workers’ livelihoods. Below, we have collected the top five issues highlighted in the study that show why this technology is a risky choice: 1. Incineration costs more than recycling. How incineration may be promoted: Incineration is a good economic decision because it reduces the costs associated with landfill operations while also creating energy that can be used by the community. The reality: • In 2016, the World Energy Council reported that, “energy generation from waste is a costly option, in comparison with other established power generation sources.” • Setting up an incineration project requires steep investment costs from the municipality. • For incineration projects to remain financially stable long-term, high fees are required, which place a burden on municipal finances and lead to sharp increases in user fees. • If incinerators are not able to collect enough burnable waste, they will burn other fuels (gas) instead. Contract obligations can force a municipality to make up the difference if an incinerator doesn’t burn enough to create the needed amount of energy.
    [Show full text]
  • Land Application of Industrial Waste
    Land Application of Industrial Waste This document is intended for use by persons or operations that generate industrial waste suitable for land application to help them determine what type(s) of regulatory oversight and/or permit is required for land application. Land application of sewage sludge (biosolids), animal manure, and petroleum contaminated soil are regulated separately from other wastes and are not the focus of this document. 1. Is the material a fertilizer or soil conditioner? Is the material managed as a valuable commodity, i.e. does the generator sell the material? Element Percent Is the intent of land applying the material to replace or offset the use of more traditional fertilizers or soil Calcium (Ca) 1.00 conditioners? Are claims or guaranties made to land owners Magnesium (Mg) 0.50 concerning the nutrient value? Sulfur (S) 1.00 Do the N, P, and K, values equal 20 when added Boron (B) 0.02 together? Chlorine (Cl) 0.10 Is the material capable of changing the pH of the soil? Cobalt (Co) 0.0005 When added to the soil or applied to plants would the Copper (Cu) 0.05 material produce a favorable growth, yield or quality of Iron (Fe) 0.10 crop or soil flora or fauna or other improved soil Manganese (Mn) 0.05 characteristics? Molybdenum (Mo) 0.0005 Does the material provide any of the following plant Sodium (Na) 0.10 nutrients at or above the level indicated in the chart Zinc (Zn) 0.05 above? If the answer to one or more of these questions is “yes” then it is possible the material could be registered and regulated by the Iowa Department of Agriculture and Land Stewardship as a fertilizer or soil conditioner and not a waste.
    [Show full text]
  • Dust Emissions from Landfill Due to Deposition of Industrial Waste: a Case Study in Malmberget Mine, Sweden
    Dust Emissions from Landfill due to Deposition of Industrial Waste: A Case Study in Malmberget Mine, Sweden Qi Jia, Yi Huang, Nadhir Al-Ansari and Sven Knutsson Civil, Mining and Nature Resources Engineering of Luleå University of Technology Abstract A great amount of industrial wastes are produced in Sweden every year. In 2008 there were 97.9 million tons of wasted generated, among which 93 million tons industrial waste were produced. 64.1% of industrial wastes were deposited in the landfill sites. Dust generation is one of the most important problems associated with industrial waste and landfills. The particulate dust emissions come from the industrial waste may contain heavy metal and produce environmental problems and potential health risks. Active and passive samplers, deposition pans are common equipment to collect dust samples. Real-time monitors use laser diffraction to recording continuous dust concentration. Dust emission from Malmberget mine in Sweden was analyzed as a case study. Dust was collected by NILU deposit gauge from 26 stations. Generally speaking the amount of dust fallout was decreasing with time because of implemented dust control methods. During the period August 2009 to August 2010, among all the measuring stations through the year, the maximum and the minimum value were 1284 g/100m2/30d and 9 g/100m2/30d. Two sources of dust generation were identified. The first was located close to the open pit, and the second near the current mining industrial center. The dust generation due to road construction was calculated. On the other hand dust generation was also closely related to weather conditions.
    [Show full text]
  • Health Effects of Residence Near Hazardous Waste Landfill Sites: a Review of Epidemiologic Literature
    Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature Martine Vrijheid Environmental Epidemiology Unit, Department of Public Health and Policy, London School of Hygiene and Tropical Medicine, London, United Kingdom This review evaluates current epidemiologic literature on health effects in relation to residence solvents, polychlorinated biphenyls (PCBs), near landfill sites. Increases in risk of adverse health effects (low birth weight, birth defects, certain and heavy metals, have shown adverse effects types of cancers) have been reported near individual landfill sites and in some multisite studies, on human health or in animal experiments. and although biases and confounding factors cannot be excluded as explanations for these A discussion of findings from either epi­ findings, they may indicate real risks associated with residence near certain landfill sites. A general demiologic or toxicologic research on health weakness in the reviewed studies is the lack of direct exposure measurement. An increased effects related to specific chemicals is beyond prevalence of self-reported health symptoms such as fatigue, sleepiness, and headaches among the scope of this review. residents near waste sites has consistently been reported in more than 10 of the reviewed papers. It is difficult to conclude whether these symptoms are an effect of direct toxicologic action of Epidemiologic Studies on chemicals present in waste sites, an effect of stress and fears related to the waste site, or an Health Effects of Landfill Sites risks to effect of reporting bias. Although a substantial number of studies have been conducted, The majority of studies evaluating possible is insufficient exposure information and effects health from landfill sites are hard to quantify.
    [Show full text]
  • Appendix a Basics of Landfill
    APPENDIX A BASICS OF LANDFILL GAS Basics of Landfill Gas (Methane, Carbon Dioxide, Hydrogen Sulfide and Sulfides) Landfill gas is produced through bacterial decomposition, volatilization and chemical reactions. Most landfill gas is produced by bacterial decomposition that occurs when organic waste solids, food (i.e. meats, vegetables), garden waste (i.e. leaf and yardwaste), wood and paper products, are broken down by bacteria naturally present in the waste and in soils. Volatilization generates landfill gas when certain wastes change from a liquid or solid into a vapor. Chemical reactions occur when different waste materials are mixed together during disposal operations. Additionally, moisture plays a large roll in the speed of decomposition. Generally, the more moisture, the more landfill gas is generated, both during the aerobic and anaerobic conditions. Landfill Gas Production and Composition: In general, during anaerobic conditions, the composition of landfill gas is approximately 50 percent methane and 50 percent carbon dioxide with trace amounts (<1 percent) of nitrogen, oxygen, hydrogen sulfide, hydrogen, and nonmethane organic compounds (NMOCs). The more organic waste and moisture present in a landfill, the more landfill gas is produced by the bacteria during decomposition. The more chemicals disposed in a landfill, the more likely volatile organic compounds and other gasses will be produced. The Four Phases of Bacterial Decomposition: “Bacteria decompose landfill waste in four phases. The composition of the gas produced changes with each of the four phases of decomposition. Landfills often accept waste over a 20-to 30-year period, so waste in a landfill may be undergoing several phases of decomposition at once.
    [Show full text]
  • Introduction to Municipal Solid Waste Disposal Facility Criteria C R Training Module Training
    Solid Waste and Emergency Response (5305W) EPA530-K-05-015 A R Introduction to Municipal Solid Waste Disposal Facility Criteria C R Training Module Training United States Environmental Protection September 2005 Agency SUBTITLE D: MUNICIPAL SOLID WASTE DISPOSAL FACILITY CRITERIA CONTENTS 1. Introduction ............................................................................................................................. 1 2. Regulatory Summary .............................................................................................................. 2 2.1 Subpart A: General Requirements ................................................................................... 3 2.2 Subpart B: Location Restrictions ..................................................................................... 6 2.3 Subpart C: Operating Criteria .......................................................................................... 8 2.4 Subpart D: Design Criteria ..............................................................................................12 2.5 Subpart E: Groundwater Monitoring and Corrective Action ..........................................12 2.6 Subpart F: Closure and Post-Closure Care ......................................................................17 2.7 Subpart G: Financial Assurance Criteria .........................................................................19 Municipal Solid Waste Disposal Facility Criteria - 1 1. INTRODUCTION This module provides a summary of the regulatory criteria for municipal solid waste
    [Show full text]
  • Inert Landfill Operations Inert Waste Definition
    Inert Landfill Operations Inert Waste Definition North Dakota Administrative Code 33-20-01.1-03 (26) defines inert waste as: “Inert waste” means nonputrescible solid waste which will not generally contaminate water or form a contaminated leachate. Inert waste does not serve as food for vectors. Inert waste includes, but is not limited to: construction and demolition material such as metal, wood, bricks, masonry and cement concrete; asphalt concrete; metal; tree branches; bottom ash from coal fired boilers; and waste coal fines from air pollution control equipment. Acceptable Wastes for Disposal? Yes (although concrete could No (aerosol cans, chemical be recycled) containers and electronics are not inert) Acceptable Wastes for Disposal? No (household waste could attract No (could attract vectors, vectors, create leachate putrescible) and/or be putrescible) Waste Collected for Non-Disposal Management • Major Appliances: – Freezers, Refrigerators, Ovens, Water Heaters, etc. – May require Freon removal with licensed equipment or removal of residual liquids – Aka “White Goods” • Scrap Metal Waste Collected for Non-Disposal Management • Grass and Leaves: – Manage by Composting – Separate from Burn Pile and Disposal Area – Soil Amendment for Cover or for Contractor/Resident Landscaping Projects – Run-off Management Waste Collected for Non-Disposal Management • Electronics*: No! – Challenging waste to recycle: • Storage • Outlet • May Contain Heavy Metals and Other Toxic Substances – Aka “E-Waste” or “Brown Goods” – Recycling Facilities and MSW
    [Show full text]
  • Landfills Are Bad, but Incinerators (With Ash Landfilling) Are Worse
    Landfills are bad, but incinerators (with ash landfilling) are worse Incinerators do not avoid landfills. For every 100 tons of trash burned, 30 tons become toxic ash that goes to landfills. The other 70 tons don’t turn into energy, but become air pollution. In terms of air pollution, and groundwater impacts, burning waste then burying ash is far worse than direct landfilling, and both are worse than a Zero Waste approach.1 A Zero Waste approach means zero incineration and at least 90% reduction from landfilling, with residuals biologically stabilized prior to landfilling, to minimize odors, leachate, gas formation and toxic migration. The most recent data comparing incinerators to landfills is from air emissions data provided by the Pennsylvania Department of Environmental Protection (DEP). For 2017, this includes data on all six trash incinerators in PA and 17 landfills in DEP’s southeast and southcentral regions. Incinerators are __ Pollutant (all data in tons) Incinerators Landfills times as polluting Greenhouse Gases (CO2e) 482,770 268,763 1.8 Total Health Damaging Pollution 1,975 1,236 1.6 Carbon Monoxide (CO) 119 22 5 Hydrochloric Acid (HCl) 17 1 21 Nitrogen Oxides (NOx) 625 6 105 Particulate Matter, Condensable 25 1 17 Particulate Matter (PM10) 26 17 1.6 Fine Particulate Matter (PM2.5) 17 4 5 Sulfur Oxides (SOx) 55 3 19 Total Suspended Particulate (TSP) 2,178 2,486 0.88 Volatile Organic Compounds (VOC) 3 9 0.34 This shows that incineration is 80% worse than landfills for the climate, and that other pollutants that directly harm human health are 60% worse from incineration.
    [Show full text]
  • Long Range Solid Waste Management Plan Environmental Assessment
    Long Range Solid Waste Management Plan Environmental Assessment Appendix H – Design and Operations Report August 2007 Long Range Solid Waste Management Plan Environmental Assessment Appendix H – Design and Operations Report - August 2007 TABLE OF CONTENTS Page 1.0 INTRODUCTION .............................................................................................. H-1 1.1 Purpose and Scope ............................................................................... H-1 1.2 Regulatory Requirements ...................................................................... H-1 1.3 Background.......................................................................................... H-10 1.4 Description of the Undertaking............................................................. H-11 2.0 LANDFILL EXPANSION SITE DESCRIPTION.............................................. H-13 2.1 Site Location ........................................................................................ H-13 2.2 Site Boundaries ................................................................................... H-13 2.3 Land Use ............................................................................................. H-13 2.4 Topography.......................................................................................... H-13 2.5 Hydrology............................................................................................. H-14 2.6 Hydrogeology....................................................................................... H-14 2.7 Archaeology........................................................................................
    [Show full text]